Modulation of trout 7-ethoxyresorufin-O-deethylase (EROD) activity by estradiol and octylphenol.

Estrogens appear to have a modulating effect on the expression of cytochrome P4501A (CYP1A) in fish. A number of in vivo studies have demonstrated that hepatic CYP1A expression in females decrease during sexual maturation when plasma levels of 17 beta-estradiol (E2) increase, or in cases when the fish in injected with E2. Since a number of environmental contaminants have weak estrogen-like activities, the question arises if these compounds are able to modulate CYP1A expression as well. In the present study, we used in vitro monolayer cultures of rainbow trout, Oncorhynchus mykiss, liver cells to compare concentration-dependent (10(-9) to 10(-5) M) effects of the natural steroid E2 and the non-steroidal xenoestrogen 4-tert-octylphenol (OP) on CYP1A-catalyzed 7-ethoxyresorufin-O-deethylase (EROD) activity. The concentration dependency of the estrogenic activity of the two test compounds was assessed by determination of hepatocellular vitellogenin (Vg) release into the culture medium. Exposure of hepatocytes to E2 concentrations of 10(-8) M and higher led to a significant inhibition of basal cellular EROD activity. On the contrary, exposure to OP did not result in an inhibition of EROD activity, even at OP concentrations (10(-6) M, 10(-5) M) which were associated with a significant induction of Vg synthesis.     

Inhibitory effects of divalent metal ions on liver microsomal 7-ethoxyresorufin O-deethylase (EROD) activity of leaping mullet

The purpose of the present study was to elucidate in vitro effects of Hg(2+), Zn(2+), Ni(2+) and Cd(2+) on cytochrome P4501A1 (CYP1A1) dependent EROD activities in leaping mullet liver microsomes. Fish captured from the most polluted part of Izmir Bay, had highly elevated EROD activities, and induced CYP1A1 protein levels as determined by Western blotting. Although all of the metal ions caused inhibition of the initial velocity of the reaction, Hg(2+) and Cd(2+) exhibited much higher inhibitory effect at lower concentrations and they were evidently more potent inhibitors than others. The inhibitor concentration giving 50% inhibition (IC(50) values) of Zn(2+), Ni(2+), Cd(2+) and Hg(2+) of initial EROD activity were 107, 16, 1.3 and 0.15 micromolar, respectively. Glutathione (GSH) at 0.5 mM final concentration, completely reversed Ni(2+) and Cd(2+) inhibition of EROD activity indicating the protective action of GSH.     

Interaction of CYP1A1 inducers in liver of rainbow trout and eelpout

The hepatic CYP1A1 (ethoxyresorufin-O-deethylase (EROD) and protein level) in rainbow trout and eelpout was induced by isosafrole, β-naphthoflavone, 3,3′,4,4′-tetrachlorobiphenyl and mixtures of two of the compounds. A potentiation effect of the CYP1A1 response was observed when isosafrole was given together with β-naphthoflavone, but not when isosafrole was given with 3,3′,4,4′-tetrachlorobiphenyl.     

Inhibitory effects of divalent metal ions on liver microsomal 7-ethoxyresorufin O-deethylase (EROD) activity of leaping mullet

The purpose of the present study was to elucidate in vitro effects of Hg²⁺, Zn²⁺, Ni²⁺ and Cd²⁺ on cytochrome P4501A1 (CYP1A1) dependent EROD activities in leaping mullet liver microsomes. Fish captured from the most polluted part of Izmir Bay, had highly elevated EROD activities, and induced CYP1A1 protein levels as determined by Western blotting. Although all of the metal ions caused inhibition of the initial velocity of the reaction, Hg²⁺ and Cd²⁺ exhibited much higher inhibitory effect at lower concentrations and they were evidently more potent inhibitors than others. The inhibitor concentration giving 50% inhibition (IC₅₀ values) of Zn²⁺, Ni²⁺, Cd²⁺ and Hg²⁺ of initial EROD activity were 107, 16, 1.3 and 0.15 micromolar, respectively. Glutathione (GSH) at 0.5 mM final concentration, completely reversed Ni²⁺ and Cd²⁺ inhibition of EROD activity indicating the protective action of GSH.     

Characterization and induction of cytochrome P-450 in the rainbow trout kidney

Cytochrome P-450 monooxygenases catalyze the biotransformation of a great variety of foreign, as well as endogenous, lipid-soluble compounds to more water-soluble products. As in mammals, highest concentration of cytochrome P-450 in fish is found in the liver. However, previous studies have indicated that fish kidney contains relatively high cytochrome P-450-mediated activities.^1,2 We have therefore prepared and characterized subcellular fractions from the kidney of rainbow trout suitable for studies on cytochrome P-450-dependent reactions. Furthermore, as in the liver, several cytochrome P-450-mediated reactions in the kidney were induced following treatment of the fish with β-naphthoflavone.     

Disposition and metabolism of 2,3,7,8-tetrachlorodibenzofuran (TCDF) in rainbow trout

In order to elucidate the metabolic fate of 2,3,7,8-tetrachlorodibenzofuran (TCDF) in fish and to thereby facilitate the assessment of the risks posed by this environmental toxin, we determined the whole body half-life, tissue distribution and metabolism of [³H TCDF in rainbow trout (Onchorynchus mykiss), treated orally. A whole body biphasic elimination pattern resulted in the excretion of 60% of the administered chemical during the first 3 days, after which a much slower elimination-rate (half-life = 14 days) was observed. Significant amounts of water-soluble metabolites were found in both bile and liver. Of the TCDF-derived radioactivity in bile, approximately 50% represented glucuronide conjugates, predominantly 4-hydroxy-2,3,7,8-TCDF: substantial amounts of the sulfate conjugate of this same metabolite were also present. Except at early time points, muscle contained the predominant fraction of TCDF-derived radioactivity, amounting to 25–65% of the total radioactivity present in the fish. More than 95% of the radioactivity present in muscle represented unmetabolized TCDF.     

Migratory behaviour of spawning rainbow trout (Oncorhynchus mykiss) in the Tongariro River,New Zealand,after habitat alteration

The movements of 92 adult rainbow trout (Oncorhynchus mykiss) from Lake Taupo into the Tongariro River, New Zealand, were monitored using radio‐telemetry every 3 days during the main spawning period between May and November 2003. This study repeated one previously conducted in 1995. Differences in spawning site preference and resting locations between 1995 and 2003 probably reflect differences in the nature of the river as a result of major natural floods that occurred in 1998. Average migration times were slower than in 1995 and the correlation between flow and mean daily movement was less distinct owing to the dry and settled weather during July and August, although fish did respond to freshets when they occurred. Peak movement occurred between 1600 and 2000 h NZ Standard Time with no movement occurring between midnight and 0400. Fish adjusted their movement in response to changing photoperiod. Nineteen fish were observed above the mouths of natal tributary streams for several weeks in the main river stem before entering these tributaries.     

Immunohistochemical localization of cytochrome P-450E in liver, gill and heart of scup (Stenotomus chrysops) and rainbow trout (Salmo gairdneri)

Monoclonal antibody directed against a major β-naphthoflavone (BNF)-induced form of teleost cytochrome P-450, P-450E (equivalent to P-450c in rat) was used to immunolocalize this enzyme in liver, gill and heart of scup and trout. Liver sections from both species showed P-450E in the cytoplasm of hepatocytes. No regional differences were observed which might indicate zonation of cytochrome P-450E within subpopulations of hepatocytes. Scup exocrine pancreatic cells were only weakly positive. In the gill of both fish, cytochrome P-450E was restricted to the endothelium (pillar cells) of secondary lamellae, where fluorescence appeared as a chain in longitudinal sections through lamellae and as star-shaped clusters in en face views. Sections of ventricular wall in both species revealed P-450E was restricted to endothelium at margins of muscle bands limiting heart ventricular lumen. Localization in the specific cells of these and other organs may be fundamentally important in understanding the role of cytochrome P-450E.     

Bioconcentration and distribution of 4-tert-octylphenol residues in tissues of the rainbow trout (Oncorhynchus mykiss)

Branched chain alkylphenols are weak oestrogen mimics which are present in the aquatic environment and have been implicated in the feminisation of fish. This study reports the biotransformation, bioconcentration and tissue distribution of the xenoestrogen 4-tert-octylphenol (t-OP) in juvenile rainbow trout. Fish were exposed for 10 days to a concentration of 4 micrograms/l of [14C] t-OP in a flow-through system and were sampled after 1, 4, 7 and 10 days of exposure. t-OP residues were extracted from all tissues and analysed by radio-high-performance liquid chromatography. After 1 day of exposure radioactive residues were detected in all tissues and reached steady state conditions in the whole fish after 4 days of exposure. The concentration of t-OP residues were highest in bile, followed by faeces, pyloric caeca, liver and intestine. In these tissues the majority of alkylphenol was in the form of two metabolites which were identified by gas chromatography-mass spectroscopy as the glucuronide conjugates of t-OP and t-octylcatechol. t-OP accumulated as the parent compound in fat with a bioconcentration factor (BCF) of 1190, and in brain, muscle, skin, bone, gills, and eye with BCFs of between 100 and 260. This study suggests that exposure to water-borne alkylphenols results in rapid conjugation and elimination of the chemical via the liver/bile route, but that high amounts of the parent xenoestrogen can accumulate in a variety of other fish tissues.     

Effect of cortisol and urea on flavin monooxygenase activity and expression in rainbow trout,Oncorhynchus mykiss

Expression of flavin-containing monooxygenase(s) (FMO) correlates with salinity exposure in certain species of euryhaline fish, such as the rainbow trout, Oncorhynchus mykiss. The mechanism(s) by which salinity regulates FMO is unclear. Adult rainbow trout were infused through the dorsal aorta with either cortisol or urea. At 500 ng/ml, cortisol caused a significant increase in FMO-catalyzed thiourea oxidase activity in gill and liver microsomes. FMOI expression, however, was significantly increased by the high cortisol dose only in gill microsomes. The levels of TMAO and urea were not altered by cortisol. In the liver, urea infusion caused an increase in hepatic FMO activity. FMO expression and activity correlated with elevated tissue urea levels, but TMAO concentrations were not related. These results indicate that FMO expression and activity may be partially controlled by the osmoregulatory/stress hormone. cortisol, and concentrations of the organic osmolyte, urea, in the rainbow trout.     

Effects of three fungicides alone and in combination on glutathione S-transferase activity (GST) and cytochrome P-450 (CYP 1A1) in the liver and gill of brown trout (Salmo trutta)

In order to evaluate the gill glutathione S-transferase (GST) activity as a biomarker of effect of fungicide exposure in juvenile brown trout (Salmo trutta), the fungicides propiconazole [(R,S)-1-[2-(2,4-diclophenyl)-4-propyl-1,3-dioolan-2-ylmetyl]-1H-1,2,4-triazole] and fenpropimorph [(+/-)-cis-4-[3-(4-tert-butylphenyl)-2-metyl propyl]-2,6 dimetylmorfolinc] were administrated in the water separately and together in a static system (80 microg/l for each pesticide) for 5 days. The combined fungicides gave a significant decrease in gill GST activity towards 1-chloro-2,4-dinitrobenzene (CDNB), whilst hepatic GST-activity was not significantly changed. Furthermore, continuous exposure to 540 ug/l thiabendazole[2-(thiazol-4'-yl)benzimidazole] in a flow-through system for 4 days significantly increased the gill glutathione S-transferase (GST) activity towards CDNB, whilst hepatic GST and cytochrome P450 (CYP 1A) activities were not increased by the treatment.     

Some effects of eutrophication and the removal of aquatic plants by grass carp (Ctenopharyngodon idella) on rainbow trout (Salmo gairdnerii) in Lake Parkinson,New Zealand

Temporary removal of aquatic plants in Lake Parkinson, a small, eutrophic dune lake, resulted in a number of changes to the population of stocked rainbow trout (Salmo gairdnerii). During each summer the lake stratified and low oxygen levels limited the distribution of trout to shallow (0–4 m) surface waters. In the first summer following weed removal the numbers of black shags (Phallacrocorax carbo) counted at the lake increased, and their predation resulted in a decline in trout density. However, the growth rate and condition of the trout population then exceeded that of trout present before weed removal. During the second summer after weed removal a cladoceran bloom was followed by low phytoplankton levels and high ammonia concentrations. A prolonged calm compounded this situation with the result that oxygen levels in bottom and surface waters dropped below 2 ppm. These low oxygen levels eliminated the trout population, but other fish species present survived. Elimination of aquatic plants affected the population dynamics of other fish species in the lake with potential implications for the trout. The experiment demonstrated the importance of weed beds in maintaining a stable fish community in lakes such as Lake Parkinson.     

Tag loss and movement of stocked yearling rainbow trout (Oncorhynchus mykiss) in southwestern Australia

Rainbow trout, Oncorhynchus mykiss, have been stocked in southwestern Australia since the 1930s. Trials at a research station maintained 868 tagged yearling O. mykiss (age: 14 months; standard length: 208 mm) for up to 375 days. The mean tag loss rate was 0.12% ± 0.040% per day for both single- and double-tagged fish. The tag loss rate was used to interpret tag return data from 7030 single-tagged yearlings stocked into three river systems in southwestern Australia. Recaptures indicated that O. mykiss survived into their second season in all rivers, with the maximum time at liberty of 21 months (longevity of at least 35 months). Upstream and downstream movements of O. mykiss increased with time, although 29% of recaptures were reported from the stocking site. Significantly more O. mykiss were recaptured from the Warren River, and differences remained even when corrected for stocking levels; angler effort had a marginal effect on return rates. Higher return rates from the Warren River may be due to availability of suitable habitat (stream cover, cooler water) for O. mykiss. Results allow the stocking regime to be reviewed to improve fishery performance.     

Effects of petroleum hydrocarbons on the hepatic cytochrome P450 1A1 system in rainbow trout

Effects on the hepatic cytochrome P450 1A1 system were investigated in juvenile rainbow trout i.p. injected with three different aromatic containing fractions: kerosene, light gas oil or heavy gas oil, originated from distilled North Sea crude oil. Kerosene treatment resulted in no effect on the P450 1A1 system, light gas oil injection caused a weak induction of EROD activities and heavy gas oil treatment resulted in a prominent induction of EROD activities as well as accumulation of CYP1A1 mRNA and P450 1A1 protein levels. The effects of heavy gas oil were compared with effects of β-napthoflavone (β-NF) on the P450 1A1 system. It was obvious that important discrepancies seemed to exist between EROD activities and corresponding CYP1A1 mRNA and P450 1A1 levels in rainbow trout treated with either heavy gas oil or β-NF i.e. heavy gas oil treatment resulted in higher specific EROD activities (EROD/P450 1A1) compared to β-NF. GC-MS analyses revealed that liver and bile from heavy gas oil treated rainbow trout in addition to naphthalene also contained polycyclic aromatic hydrocarbons such as phenanthrenes, anthracene, pyrenes, fluoranthene benz(a)anthracene and chrysene, while none of these compounds were detected in control trout.     

Seasonal variation of hepatic EROD activity in flounder (Platichthys flesus) in the Dutch Wadden Sea

The use of hepatic 7-ethoxyresorufin O-deethylase (EROD) activity in flounder (Platichthys flesus) as a potential biomarker of marine pollution by organic chemicals (as indicated by hepatic PCB-153 concentration) was investigated in the Dutch Wadden Sea in 1989 and 1990. Particular attention was paid to the seasonal variation. The results indicate that EROD activity was reasonably stable during the year, except for a period in January–February when a marked peak occurred. This peak coincided with the absence of mature flounder from the sampling area probably due to the spawning migration. Generally a good relationship existed between hepatic EROD activity and PCB-153 concentration, with one exception. During the period January–April 1990 a peak in PCB-153 concentration occurred immediately after the observed peak in EROD activity. It is concluded that the best period for monitoring EROD activity in flounder is the summer, corresponding to the non-migratory period of the species.     

The effect of estrogen on cadmium distribution in rainbow trout (Oncorhynchus mykiss)

The effects of injections of 17β-estradiol (E2) and Cd, on the distribution of Cd and the induction of metallothionein (MT) mRNA and vitellogenin mRNA was investigated. Bone and liver were the main organs accumulating Cd. However, E2 redirected the metal accumulation from the bone and liver to the gill, gut and muscle upon exposure to E2. Cd did not induce the hepatic MT mRNA levels in animals treated with E2. The VTG mRNA levels were also reduced following co-injection of E2 and Cd. However, the kidney responded to Cd exposure by upregulating MT mRNA even in the presence of E2 treatment. In the liver the reduced MT mRNA induction led to a redistribution of CD from MT to non-MT proteins. The toxicological significance of these alterations in Cd handling remains to be determined.     

EROD activities of liver in Mugil so-iuy exposed to benzo (a)pyrene, pyrene and their mixture

Abstract-The effects on hepatic EROD (7-ethoxyresorufin O-deethylase) in Mugil so-iuy exposedto benzo(a)pyrene (BaP), pyrene and their mixtures of equal concentration were investigated, at con-centrations of 0.1, 1.0, 5.0, 10.0, 50.0 μg/dm~3, in experimental condition. Time-effects and dose-response of the biochemical indexs were observed. The results showed that the hepatic EROD activitieswere induced by the exposure of BaP, pyrene and their mixtures at high concentration. Dose-responseconnections were that the hepatic EROD activities were elevated with increasing concentration of the pol-lutants. The combined effect of BaP and pyrene at 1:1 concentration ratio on hepatic EROD activity wasantagonism.